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首页> 外文期刊>Environmental Science & Technology >Perchlorate Production by Photodecomposition of Aqueous Chlorine Solutions
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Perchlorate Production by Photodecomposition of Aqueous Chlorine Solutions

机译:通过光解氯水溶液生产高氯酸盐

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摘要

Aqueous chlorine solutions (denned as chlorine solutions (Cl_(2,T)) containing solely or a combination of molecular chlorine (Cl_2), hypochlorous acid (HOG), and hypochlorite (OCl~-)) are known to produce toxic inorganic disinfection byproduct (e.g., chlorate and chlorite) through photoactivated transformations. Recent reports of perchlorate (ClO_4~-) production-a well-known thyroid hormone disruptor- from stored bleach solutions indicates the presence of unexplored transformation pathway(s). The evaluation of this potential ClO_4~- source is important given the widespread use of aqueous chlorine as a disinfectant. In this study, we perform detailed rate analysis of ClO_4~- generation from aqueous chlorine under varying environmental conditions including ultraviolet (UV) light sources, intensity, solution pH, and Cl_(2,T) concentrations. Our results show that ClO_4~- is produced upon UV exposure of aqueous chlorine solutions with yields ranging from 0.09 × 10~(-3) to 9.2 × 10~(-3)% for all experimental conditions. The amount of ClO_4~- produced depends on the starting concentrations of Cl_(2,T) and ClO_3~-, UV source wavelength, and solution pH, but it is independent of light intensity. We hypothesize a mechanistic pathway derived from known reactions of Cl_(2,T) photodecomposition that involves the reaction of Cl radicals with ClO_3~- to produce ClO_4~- with calculated rate coefficient (k_(ClO4-)) of (4-40) × 10s M~(-1) s~(-1) and (3-250) × 105 M~(-1) s~(-1) for UV-B/C and UV-A, respectively. The measured ClO_4~- concentrations for both UV-B and UV-C experiments agreed well with our model (R~2 = 0.88-0.99), except under UV-A light exposure (R~2 = 0.52-0.93), suggesting the possible involvement of additional pathways at higher wavelengths. Based on our results, phototransformation of aqueous chlorine solutions at concentrations relevant to drinking water treatment would result in ClO_4~- concentrations (~0.1 μg L~(-1)) much below the proposed drinking water limits. The importance of the hypothesized mechanism is discussed in relation to natural ClO_4~-formation by atmospheric transformations.
机译:已知氯水溶液(浓缩为仅包含或包含分子氯(Cl_2),次氯酸(HOG)和次氯酸盐(OCl〜-)的氯溶液(Cl_(2,T))会产生有毒的无机消毒副产物(例如氯酸盐和亚氯酸盐)通过光活化的转化。最近从储存的漂白液中产生高氯酸盐(ClO_4〜-)(一种众所周知的甲状腺激素破坏剂)的报告表明存在未探索的转化途径。考虑到氯水溶液作为消毒剂的广泛使用,对这种潜在的ClO 4-来源的评估很重要。在这项研究中,我们进行了详细的速率分析,分析了在不同的环境条件下,从氯水溶液中生成ClO_4〜-的情况,包括紫外线(UV)光源,强度,溶液pH值和Cl_(2,T)浓度。我们的结果表明,ClO_4〜-是在氯水溶液紫外线照射下产生的,在所有实验条件下,其收率范围为0.09×10〜(-3)至9.2×10〜(-3)%。产生的ClO_4〜的量取决于Cl_(2,T)和ClO_3〜-的起始浓度,紫外线源的波长和溶液的pH值,但与光强度无关。我们假设了从已知的Cl_(2,T)光分解反应衍生的机理途径,该机理涉及Cl自由基与ClO_3〜-产生ClO_4〜-的反应,计算出的速率系数(k_(ClO4-))为(4-40)对于UV-B / C和UV-A,分别为10s M〜(-1)s〜(-1)和(3-250)×105 M〜(-1)s〜(-1)。在UV-B和UV-C实验中测得的ClO_4〜-浓度与我们的模型(R〜2 = 0.88-0.99)很好地吻合,除了在UV-A光照下(R〜2 = 0.52-0.93),这表明在更高波长处可能涉及其他途径。根据我们的结果,与饮用水处理有关的浓度的氯水溶液发生光转化会导致ClO_4〜-的浓度(〜0.1μgL〜(-1))大大低于建议的饮用水限值。讨论了假设的机制与通过大气转化自然生成ClO_4〜有关的重要性。

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  • 来源
    《Environmental Science & Technology》 |2012年第21期|11635-11643|共9页
  • 作者单位

    Environmental Sciences Division, Oak Ridge National Laboratory, Oak Ridge, Tennessee, United States;

    Depratment of Civil and Environmental Engineering, Texas Tech University, Lubbock, Texas 79409-1023, United States;

    Department of Mathematics, Our Lady of the Lake University, San Antonio, Texas 78207, United States;

    Department of Civil, Architectural and Environmental Engineering, University of Texas at Austin, Austin, Texas, United States;

    Environmental Sciences Division, Oak Ridge National Laboratory, Oak Ridge, Tennessee, United States;

    Depratment of Civil and Environmental Engineering, Texas Tech University, Lubbock, Texas 79409-1023, United States;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
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  • 正文语种 eng
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